| Literature DB >> 34064949 |
Win Wah1, Rob G Stirling2,3, Susannah Ahern1, Arul Earnest1.
Abstract
Predicting lung cancer cases at the small-area level is helpful to quantify the lung cancer burden for health planning purposes at the local geographic level. Using Victorian Cancer Registry (2001-2018) data, this study aims to forecast lung cancer counts at the local government area (LGA) level over the next ten years (2019-2028) in Victoria, Australia. We used the Age-Period-Cohort approach to estimate the annual age-specific incidence and utilised Bayesian spatio-temporal models that account for non-linear temporal trends and area-level risk factors. Compared to 2001, lung cancer incidence increased by 28.82% from 1353 to 1743 cases for men and 78.79% from 759 to 1357 cases for women in 2018. Lung cancer counts are expected to reach 2515 cases for men and 1909 cases for women in 2028, with a corresponding 44% and 41% increase. The majority of LGAs are projected to have an increasing trend for both men and women by 2028. Unexplained area-level spatial variation substantially reduced after adjusting for the elderly population in the model. Male and female lung cancer cases are projected to rise at the state level and in each LGA in the next ten years. Population growth and an ageing population largely contributed to this rise.Entities:
Keywords: Bayesian; age-period-cohort; forecast; lung cancer; spatio-temporal
Year: 2021 PMID: 34064949 PMCID: PMC8151486 DOI: 10.3390/ijerph18105069
Source DB: PubMed Journal: Int J Environ Res Public Health ISSN: 1660-4601 Impact factor: 3.390
Figure 1Line plot of annual lung cancer incidence and proportion of the elderly population.
Comparison of goodness-of-fit of the Bayesian spatial-temporal models.
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| Model A (Linear & quadratic temporal terms) |
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| Model B (Autoregressive temporal terms) | 4610 |
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| Model A (Linear & quadratic temporal terms) |
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| Model B (Autoregressive temporal terms) | 4061 |
DIC; Deviance information criterion, Lower DIC indicates better model fit (Bold).
Comparison of predictive accuracy of the Bayesian spatio-temporal models.
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| Training (2001–2013) | RMSE | MAE | MAPE | DIC | RMSE | MAE | MAPE | DIC |
| Model A (Linear & quadratic temporal terms) | 1.34 | 0.71 | 3.86 | 4532 | 0.89 | 0.44 | 4.12 | 3940 |
| Model A + Smoking | 1.33 | 0.71 | 3.75 | 4478 | 0.90 | 0.45 | 4.20 | 3982 |
| Model A + Smoking + RSD | 1.34 | 0.71 | 3.79 | 4356 | 0.89 | 0.45 | 4.07 | 3995 |
| Model A + Smoking + Pollution | 1.35 | 0.73 | 4.04 | 4498 | 0.91 | 0.46 | 4.48 | 3985 |
| Model A + Smoking + Elderly | 1.38 | 0.74 | 3.85 | 4578 | 0.96 | 0.48 | 4.19 | 4031 |
| Model A + Smoking + Elderly + Pollution | 1.39 | 0.75 | 3.89 | 4575 | 0.94 | 0.48 | 4.44 | 4029 |
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| Model A (Linear & quadratic temporal terms) |
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| Model A + Smoking | 8.80 | 5.91 | 40.26 | 4478 | 6.40 | 4.32 | 33.17 | 3982 |
| Model A + Smoking + RSD | 8.81 | 5.89 | 40.06 | 4356 | 6.40 | 4.34 | 33.04 | 3995 |
| Model A + Smoking + Pollution | 8.80 | 5.92 | 40.57 | 4498 | 6.41 | 4.36 | 33.83 | 3985 |
| Model A + Smoking + Elderly | 8.80 | 5.93 | 41.61 | 4578 | 6.40 | 4.34 | 33.87 | 4031 |
| Model A + Smoking + Elderly + Pollution | 8.81 | 5.94 | 41.90 | 4575 | 6.43 | 4.37 | 33.84 | 4029 |
RMSE; Root mean squared error, MAE; Mean absolute error, MAPE; Mean absolute percentage error, DIC; Deviance information criterion. Lower values of these measures indicate better prediction accuracy (Bold).
Figure 2Comparison of observed and predicted male and female lung cancer counts per year.
Figure 3Comparison of observed and predicted male lung cancer counts per year by Local Government Areas.
Figure 4Comparison of observed and predicted female lung cancer counts per year by Local Government Areas.
Figure 5Comparison of observed and predicted male lung cancer counts per year in selected Local Government Areas by remoteness category.
Figure 6Comparison of observed and predicted female lung cancer counts per year in selected Local Government Areas by remoteness category.